Resistance breakdown of PTB33
Four BPH populations collected at Hadano City, Kanagawa Prefecture, Japan, in 1966 (1966-Hadano population), Chikugo City, Fukuoka Prefecture, Japan in 1989 (1989-Chikugo population), Koshi City, Kumamoto Prefecture, Japan in 1999 (1999-Koshi population), and Koshi in 2013 (2013-Koshi) were used in infestation (Table S1). The BPH resistance of PTB33 was evaluated by the rate of females with a swollen abdomen (FSA) at five days after infestation (DAI) by the 1966-Hadano, 1989-Chikugo, 1999-Koshi, and 2013-Koshi BPH populations were 0.0%, 4.0%, 16.0%, and 55.0%, respectively, suggesting that the virulence of BPH populations increases with the collection year of BPH (Fig. 1).
QTL estimation for BPH resistance
The effective resistance QTLs to the four BPH populations were investigated in hybrid progenies derived from a cross between the susceptible varieties T65 and PTB33 (Fig. S1). The B1F2 populations were infested by the 1966-Hadano BPH population, and the B1F3 populations were infested by 1989-Chikugo, 1999-Koshi, and 2013-Koshi BPH populations (Fig. 1). The B1F2 and B1F3 populations backcrossed with T65 showed continuous distributions of FSA. The population means of FSA gradually increased with the collection year of BPH, with that of 1966-Hadano, 1989-Chikugo, 1999-Koshi, and 2013-Koshi being 33.4%, 47.0%, 68.0%, and 89.1% at 3 DAI (Fig. 1a-d) and 43.4%, 55.2%, 75.2%, and 91.7%, at 5 DAI (Fig. 1e-h), respectively. When the resistance was evaluated in female adult mortality (FAM), the BPH resistance of the population similarly decreased with the collection year of BPH (Fig. S2). FAM means in the T65 backcrossed population were found to decrease with the collection years: 35.1%, 35.2%, 19.8%, and 14.0% at 3 DAI and 52.6%, 54.4%, 32.4%, and 39.6% at 5 DAI, respectively (Fig. S2).
In the PTB33 backcrossed population, the FSA of the 1966-Hadano, 1989-Chikugo, 1999-Koshi, and 2013-Koshi BPH populations were 12.1%, 11.3%, 14.6%, and 34.5% at 3 DAI (Fig. 2a-d) and 19.8%, 20.0%, 19.8%, and 54.5%, respectively, at 5 DAI (Fig. 2e-h), respectively. FAM was 45.6%, 84.8%. 89.3%, and 35.5% at 3 DAI and 84.0%, 93.9%, 93.8%, and 55.9% at 5 DAI (Fig. S3).
Next, QTLs conferring BPH resistance were elucidated by multiple QTL mapping (MQM) for FSA at 5 DAI in four BPH populations since FSA at 5 DAI showed a larger phenotypic variance could be a suitable measure for QTL analysis. The numbers of SNP markers detected by genotyping-by-sequencing were shown in Table S1. In the T65-backcrossed populations infested by the 1966-Hadano BPH population, simple marker regression detected only one significant QTL, qFSA4a, at 6.4 Mbp on chromosome 4. Multiple QTL mapping, including qFSA4a as a covariate, detected the 2nd QTL, qFSA6, at 2.2 Mbp on chromosome 6. Several cycles of multiple QTL mapping, including all detected QTLs as covariates, were repeated until the updated genetic model did not improve the LOD value by more than 3.0 in the likelihood ratio test (see Methods). Collectively, multiple QTL mapping for FSA detected five QTLs (Table 1): qFSA4a, qFSA6, qFSA11 at 24.3 Mbp on chromosome 11, qFSA7a at 1.6 Mbp on chromosome 7, and qFSA3 at 10.3 Mbp on chromosome 3. The genetic effects of the five QTLs were estimated simultaneously: qFSA4a had the largest genetic effects, with 43.0% PVE and -28.8% additive effects; qFSA6 explained 6.5% of the PVE and an additive effect of -13.9%; qFSA11 had a PVE of 5.0% and an additive effect of 16.9%; qFSA7a had a PVE of 4.3% and an additive effect of -15.8%; and qFSA3 had the lowest PVE of 4.0% and an additive effect of -9.6%.
Next, effective QTL to the 1989-Chikugo BPH at 5 DAI was explored. All of the QTLs detected by the 1966-Hadano were not detected. Instead, qFSA4b at 13.0 Mbp on the short arm of chromosome 4 and qFSA12 at 23.5 Mbp on the long arm of chromosome 12 were involved in BPH resistance (Table 1). qFSA4b explained a PVE of 20.6% and an additive effect of -20.8%. qFSA12 explained a PVE of 11.9% and an additive effect of -15.8%. In the BC1F3 population infested by the 1999-Koshi BPH population, one QTL with a PVE of 22.6% and an additive effect of -15.3% was detected at 7.4 Mbp on chromosome 4, which seemed equivalent to qFSA4a (Table 1). No QTLs were detected in the BC1F3 population infested by the 2013-Koshi BPH population.
In the PTB33 backcrossed population, no QTLs were detected for FSA at 5 DAI in any BPH population, probably due to small phenotypic variance because almost segregating plants showed strong resistance. However, at 3 DAI, several QTLs were successfully detected (Table 2). In the BC1F3 population infested by the 2013-Koshi BPH population, qFSA6 at 2.4 Mbp on chromosome 6 and qFSA8 at 18.0 Mbp on chromosome 8 were involved in BPH resistance with additive effects of -25.7%. and -14.6%, respectively).
QTL identification in T65 genetic background
The suggested QTLs for FSA were identified using flanking SSR markers by the infestation of the 1966-Hadano BPH population at 5 DAI. In the B1F3 population derived from backcrossing with T65, plants heterozygous at the QTL and homozygous for T65 or PTB33 at the background QTL were self-pollinated to obtain B1F4 populations as the monogenic segregating populations (Fig. 3, Table S3). LOD peaks at qFSA4a, qFSA6, qFSA11, and qFSA12 exceeded over more than a 5% empirical threshold in the corresponding MSP: qFSA4a was repeatedly detected in B1F4 population #102, and the PTB33 allele was estimated to reduce 33.2% of FSA at 5 DAI; qFSA6 was identified in population B1F4 #114, with an additive effect of -26.5% for the PTB33 allele. Similarly, qFSA11 and qFSA12 were identified with additive effects of -13.2% and -11.5% for the PTB33 allele in B1F4 populations #109 and #110, respectively. The remaining three QTLs (qFSA3, qFSA4b, and qFSA7a) were not identified in these populations.
Assessment of genetic effects at QTLs responding to insect population
The reduction of genetic effects at the qFSA4a, qFSA6, qFSA11, and qFSA12 to developing virulence of the four BPH populations was statistically measured by LODi, LOD scores attributed from interaction component between QTLs and BPH populations (Table 3). The phenotypic values and genotypes of the B1F2 populations infested by 1966-Hadano BPH and the B1F3 populations infested by 1999-Koshi BPH were mixed and simultaneously solved to estimate LODi. The LODi score at qFSA4a was higher than the 5% significant threshold, implying that genetic effects at qFSA4a were different by 1966-Hadano and 1999-Koshi BPH populations. This difference is likely due to the shrinkage of the additive effect of FSA from -28.8% in the 1966-Hadano BPH to -15.3% in the 1999-Koshi BPH (Tables 1 and 3).
The LODi scores at qFSA11 did not show apparent at 5% significance level but showed significance at 10% level in population size in this study. The additive effects of the PTB33 allele at qFSA11 were -16.9% or zero (null hypothesis) by the 1966-Hadano or 1999-Koshi BPH, respectively. The LODi scores at qFSA12 implied that genetic effects were different by the BPH populations at a 10% significance level. The additive effect at the qFSA12 was significantly estimated with -11.5% for the PTB33 allele in the B1F4 monogenic segregating population infested by the 1966-Hadano BPH infestation (Table S3). However, qFSA12 was not detected in the B1F2 generation, probably because residuals were not sufficient enough to detect qFSA12 under simultaneous estimation with qFSA4a, qFSA6, qFSA11, qFSA7a, and qFSA3 in this population size. On the other hand, the interaction of qFSA6 by the BPH populations was not apparent, while qFSA6 conferred resistance by the infestation of the 1966-Hadano BPH but not to the 1999-Koshi BPH population (Table 3).
The genetic effects of the PTB33 alleles at the qFSA4a, qFSA6, qFSA11, and qFSA12 to the four BPH populations were clarified the B1F5 plants homozygous for T65 (T) and PTB33 (P) were obtained from a single heterozygous MSP of each QTL (Fig. 4) and infested by the four BPH populations. Female insects with medium swollen abdomens (MS) and non-swollen abdomens (NS) were evaluated as those with reduced growth and insects with swollen abdomen as those with normal (N) growth. Infestation with 1966-Hadano BPH revealed an apparent resistance effect of qFSA4a, qFSA11, and qFSA12 on homozygous plants for PTB33, as compared with homozygous plants for T65 in Fisher's exact test. However, the resistance effect of the PTB33 allele at qFSA11 was lost in the 1989-Chikugo insect population, while the other QTLs qFSA4a and qFSA12 were still effective. The PTB33 allele at qFSA12 lost resistance effect, whereasone at qFSA4a remained to the 1999-Koshi BPH population. However, all four QTLs lost resistance to the 2013-Koshi insect population. Therefore it was concluded that the PTB33 alleles at qFSA11, qFSA12, and qFSA4a lost resistance effects in 1989, 1999, and 2013, respectively.